JPH0751690A - Foreign matter adsorbent, carrier of adequate bacteria and their production - Google Patents

Foreign matter adsorbent, carrier of adequate bacteria and their production

Info

Publication number
JPH0751690A
JPH0751690A JP5218113A JP21811393A JPH0751690A JP H0751690 A JPH0751690 A JP H0751690A JP 5218113 A JP5218113 A JP 5218113A JP 21811393 A JP21811393 A JP 21811393A JP H0751690 A JPH0751690 A JP H0751690A
Authority
JP
Japan
Prior art keywords
foreign matter
carrier
mother liquor
foam
specific gravity
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP5218113A
Other languages
Japanese (ja)
Other versions
JP2726376B2 (en
Inventor
Katsutoshi Oshima
勝利 大島
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
OSUMAN KOGYO KK
Original Assignee
OSUMAN KOGYO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by OSUMAN KOGYO KK filed Critical OSUMAN KOGYO KK
Priority to JP5218113A priority Critical patent/JP2726376B2/en
Publication of JPH0751690A publication Critical patent/JPH0751690A/en
Application granted granted Critical
Publication of JP2726376B2 publication Critical patent/JP2726376B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PURPOSE:To make it possible to efficiently and effectively purify all kinds of foreign matter-contg. liquids contg. foreign matter and to shorten the stagnation time thereof by forming a carrier out of a foam having closed cells and having the apparent sp. gr. or true sp. gr. below the sp. gr. of the mother liquor. CONSTITUTION:A vessel 1 having its upper part opened is internally provided with a blocking plate 13. The carriers 2a which carry microorganisms, have closed cells and the apparent sp. gr. or true sp. gr. below the sp. gr. of the mother liquor in which the required foreign matter exists is packed in the lower part of the plate to form a suspended bed 2. The foreign matter-contg. liquid is filtered by an anaerobic granulated mud tank 10 when the foreign matter-contg. liquid is poured from a water spraying nozzle 4 via an introducing pipe 3 upward from the lower part in the vessel 1. Thereafter, this liquid passes a sludge granule zone 11 and is double filtered by the respective carrier zones 2 of a suspended bed 2 and the microorganisms carried therein. The microorganism-decomposition of the org. matter and nitrification are executed during this time. The foreign matter is gathered by a water collecting pipe 5 from the water surface and is discharged from a drain pipe 6.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、海洋、河川、湖沼、工
場排水等、処理を必要とするあらゆる異物含有液に含ま
れる異物を回収または除去するために用いるのに適した
異物吸着材及び異物を分解するための適性菌の担持体並
びにそれらの製造方法に関するものである。
BACKGROUND OF THE INVENTION The present invention relates to a foreign matter adsorbent suitable for use in collecting or removing foreign matter contained in any foreign matter-containing liquid that requires treatment, such as the ocean, rivers, lakes and marshes, factory wastewater, and the like. The present invention relates to a carrier for suitable bacteria for decomposing foreign substances and a method for producing them.

【0002】[0002]

【従来の技術】従来、例えば富栄養化された海洋、河
川、湖沼或いは工場排水は、赤潮、アオコ等の種々の異
常発生が激しく、その除去のために塩素による除藻と、
砂、アンスラサイトによる濾過とを併用するなどしてい
た。
2. Description of the Related Art Conventionally, for example, eutrophication of oceans, rivers, lakes and marshes or industrial wastewater has caused various abnormalities such as red tides and water-blooms.
It was used in combination with sand and anthracite filtration.

【0003】これらの藻類は、アオコに代表されるよう
に、粒子径が2〜5ミクロンと微細で、通常は群落をな
してブロックが大きいが、ポンプアップすると個々の粒
子に戻り、砂やアンスラサイトでは濾過が難しい。従っ
て、藻類を塩素の増量によって殺藻せざるを得ず、結果
的に発ガン性の強いトリハロメタンが生成される。ま
た、富栄養化された海洋、湖沼、河川では、BOD、C
OD、SS等指標要因物質の除去は凝集沈澱や、活性
炭、砂濾過の併用によって、或る程度までは達成できる
が、大量の水を高速で高性能で安価に処理することは難
しい。
[0003] These algae have a fine particle diameter of 2 to 5 microns as typified by water-bloom, and usually form a group and have a large block, but when pumped up, they return to individual particles, and sand or anthra. Filtration is difficult at the site. Therefore, algae must be killed by increasing the amount of chlorine, and as a result, highly carcinogenic trihalomethane is produced. In addition, in eutrophic oceans, lakes and rivers, BOD, C
The removal of index factor substances such as OD and SS can be achieved to some extent by coagulation sedimentation and combined use of activated carbon and sand filtration, but it is difficult to treat a large amount of water at high speed with high performance at low cost.

【0004】そこで、嫌気処理として、温度を高めて発
酵促進させる方法、上向流を用いる方法(スラッジグラ
ンケート法:VASB法)等がある。
Therefore, as the anaerobic treatment, there are a method of raising the temperature to promote fermentation, a method of using an upward flow (sludge granate method: VASB method) and the like.

【0005】上記各方法のうち、嫌気処理で温度を高め
て発酵させる方法は、下水スラッジや有害廃棄物のよう
に固形物の多い廃棄物の処理には有効であるが、廃水の
処理のような場合にはランニングコストがかさみ得策で
はない。また、VASB法はバクテリアの自己造粒を利
用して接触効率を高める方法として有効であるが、より
効率を高めるためのSS濃縮構造(汚泥造粒部)がな
く、上部の生物膜濾過の性能の付加もないため、多くの
滞留時間を要し、設備が過大となる欠点がある。
Of the above methods, the method of raising the temperature by anaerobic treatment to ferment is effective for the treatment of waste with a large amount of solids such as sewage sludge and hazardous waste. In such cases, running cost is not a good idea. In addition, the VASB method is effective as a method for increasing the contact efficiency by utilizing the self-granulation of bacteria, but there is no SS concentrating structure (sludge granulation part) to further improve the efficiency, and the performance of the biofilm filtration on the upper side. Since there is no addition of water, a long residence time is required and there is a drawback that the equipment becomes excessive.

【0006】[0006]

【発明が解決しようとする課題】このような従来技術の
問題点に鑑み、本発明の主な目的は、海洋、河川、湖
沼、工場排水等、処理を必要とするあらゆる母液を効率
的かつ効果的に浄化可能な異物吸着材、適性菌の担持体
または商品製造過程に於ける金属イオン交換後の非鉄金
属等を回収する有価物の回収材及びそれらの製造方法を
提供することにある。
In view of the above problems of the prior art, the main object of the present invention is to efficiently and effectively treat any mother liquor that requires treatment, such as the ocean, rivers, lakes, and factory wastewater. (EN) Provided are a foreign matter adsorbent that can be purified, a carrier for suitable bacteria, or a valuable material recovery material for recovering non-ferrous metals and the like after metal ion exchange in the product manufacturing process, and a manufacturing method thereof.

【0007】[0007]

【課題を解決するための手段】上述した目的は本発明に
よれば、回収または除去を必要とする異物が存在する母
液に接触させることにより前記母液に含まれる異物を吸
着する異物吸着材及びこれら異物を分解するための適性
菌を担持させるための担持体であって、独立発泡による
独立気泡を有する見かけ比重または真比重が前記母液の
比重以下の発泡体からなることを特徴とする異物吸着材
及び適性菌の担持体を提供することにより達成される。
これらは、原料の樹脂材を混練しつつ独立発泡させ、内
部に独立気泡を形成するように製造すると良い。
According to the present invention, the above-mentioned object is to adsorb foreign matter contained in the mother liquor by adsorbing the foreign matter contained in the mother liquor by contacting with the mother liquor containing the foreign matter requiring recovery or removal. A carrier for supporting suitable bacteria for decomposing foreign matter, comprising a foam having an apparent specific gravity or true specific gravity having independent bubbles due to independent foaming, which is equal to or lower than the specific gravity of the mother liquor. And by providing a support for suitable bacteria.
It is advisable to manufacture these so that the raw material resin material is kneaded to be independently foamed to form closed cells inside.

【0008】[0008]

【作用】このようにすれば、例えばこの吸着材を容器の
上部に浮遊させ、最下部から上部に向けて異物含有液を
流すことによって異物を発泡体に吸着し、除去すること
ができる。また、予め微生物(適性菌)を担持させた担
持体を容器の上部に浮遊させ、最下部から上部に向けて
異物含有液を流すことによって、微生物の自己造粒が容
易であることは云うまでもなく、担持体が浮遊している
ことから異物含有液が最下部から上部微生物層(浮遊
層)にいたる間にSSの濃縮ゾーンが形成され、余剰汚
泥の造粒沈降を促すことができる。更に、発泡体を破砕
してなる吸着材または各担持体は多孔質多面体であるた
め、表面積が大きいことから浮遊層中に於ける異物含有
液との接触面積の向上が計れ、かつ担持体の場合、硝化
菌(適性菌)の増殖が促進され、即ち有機物の分解、硝
化が促進され、異物含有液の浄化能力を高めることがで
きる。また、従来法のように前処理としての加圧浮上
や、凝集沈澱処理を行う必要がなく、高濃度の異物含有
液のまま処理することができ、更に例えば水道水であれ
ば塩素処理工程を削減することができる。
By doing so, for example, the adsorbent can be adsorbed on the foam and removed by floating the adsorbent in the upper part of the container and flowing the liquid containing the foreign substance from the lowermost part to the upper part. In addition, it is easy to self-granulate the microorganisms by suspending the carrier carrying the microorganisms (appropriate bacteria) in the upper part of the container and flowing the foreign substance-containing liquid from the lowermost part to the upper part. Nonetheless, since the carrier is floating, a concentration zone of SS is formed between the lowermost part and the upper microbial layer (floating layer) of the foreign matter-containing liquid, which can promote the granulation and sedimentation of the excess sludge. Further, since the adsorbent obtained by crushing the foam or each carrier is a porous polyhedron, since the surface area is large, the contact area with the liquid containing the foreign matter in the floating layer can be improved, and the carrier In this case, the growth of nitrifying bacteria (appropriate bacteria) is promoted, that is, the decomposition and nitrification of organic substances are promoted, and the ability to purify the liquid containing foreign matter can be enhanced. Further, unlike the conventional method, it is not necessary to perform pressure floating as a pretreatment or coagulation-sedimentation treatment, and it is possible to treat the liquid containing a high-concentration foreign matter as it is. Can be reduced.

【0009】ここで、吸着材または担持体の各気泡が連
続気泡であると、吸着材または担持体に水道が形成さ
れ、吸着材の場合には吸着した異物が再び母液に流され
る心配があり、担持体の場合には適性菌を長期に亘り担
持、増殖し難いことが考えられるが、本発明吸着材また
は担持体は、その各気泡が連続せず、吸着材及び担持体
に水道が形成されない。従って、吸着材の場合には吸着
した異物が再び母液に流されるようなことがなく、担持
体の場合には適性菌を著気に亘り担持、増殖し易くな
る。また、異物の回収または除去効率に関し、独立発泡
による独立気泡を有する発泡体の表面積は連続発泡によ
る連続気泡を有する発泡体に比較して小さいことが考え
られるが、上記したように連続気泡を有する発泡体はそ
の内部に水道が形成されることからその部分は吸着及び
適性菌との接触が行われ難い。従って、異物の吸着また
は担持体に担持された適性菌との接触のために有効な表
面積(母液との接触面積)は、独立気泡を有する発泡体
(本発明吸着材または担持体)の方が連続気泡を有する
発泡体に比較して大きくなる。また、この吸着材または
適性菌の担持体が、上記発泡体を破砕することにより得
られる形成された大きさ及び形状の不揃いな多数の小片
からなることにより、母液との接触効率が向上する。
If each bubble of the adsorbent or the carrier is an open cell, water may be formed in the adsorbent or the carrier, and in the case of the adsorbent, the adsorbed foreign matter may flow into the mother liquor again. , In the case of a carrier, it is considered that suitable bacteria are supported for a long period of time and it is difficult to grow, but in the adsorbent or the carrier of the present invention, each bubble is not continuous, and water is formed in the adsorbent and the carrier. Not done. Therefore, in the case of the adsorbent, the adsorbed foreign matter does not flow into the mother liquor again, and in the case of the carrier, it becomes easy to carry and proliferate suitable bacteria in a remarkable manner. Further, regarding the efficiency of collecting or removing foreign matter, the surface area of the foam having the closed cells by the independent foaming may be smaller than that of the foam having the open cells by the continuous foaming. Since water is formed inside the foam, it is difficult for that part to be adsorbed and contact with suitable bacteria. Therefore, the surface area (contact area with the mother liquor) effective for adsorbing foreign matters or contacting the suitable bacteria carried on the carrier is larger for the foam having closed cells (the adsorbent of the present invention or the carrier). The size is larger than that of a foam having open cells. Further, since the adsorbent or the carrier of the suitable bacteria is composed of a large number of small pieces having irregular sizes and shapes formed by crushing the foam, the contact efficiency with the mother liquor is improved.

【0010】このような独立気泡を有する発泡体からな
る吸着材または担持体は、原料の樹脂材を混練しつつ低
圧で発泡させることにより得られる。
The adsorbent or carrier made of a foam having such closed cells can be obtained by kneading a resin material as a raw material and foaming at a low pressure.

【0011】[0011]

【実施例】以下、本発明の好適実施例を添付の図面につ
いて詳しく説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT A preferred embodiment of the present invention will now be described in detail with reference to the accompanying drawings.

【0012】図1は、本発明が適用された第1の実施例
を示す嫌気性菌による処理装置を模式的に示すダイヤグ
ラム図である。図に於て上部が開口する容器1内には抑
止板13が設けられ、その下部に微生物(適性菌)を担
持する見かけ比重または真比重が除去を必要とする異物
が存在する母液比重以下の担持体2a(浮遊充填材)を
充填し、浮遊層2を形成している。また、容器1の下部
には海洋、河川、湖沼、工場排水等、処理を必要とする
母液を容器1内に流し込むべく導入管3を介して散水ノ
ズル4が設けられている。容器1内の浮遊層2の上部に
は集水管5が設けられ、この処理された水を集水管5に
て集めて排水管6から排出するようになっている。加え
て、容器1の最下部には排出弁7aを有する余剰汚泥抜
き管7が設けられ、容器1の中層部には逆洗用のノズル
8が設けられている。
FIG. 1 is a schematic diagram showing a treatment apparatus using anaerobic bacteria showing a first embodiment to which the present invention is applied. In the figure, a container 1 having an open upper portion is provided with a deterrent plate 13, and an apparent specific gravity or true specific gravity carrying microbes (appropriate bacteria) is below the mother liquor specific gravity in which foreign substances need to be removed. The carrier 2a (floating filler) is filled to form the floating layer 2. Further, a sprinkling nozzle 4 is provided below the container 1 via an introduction pipe 3 in order to flow the mother liquor requiring treatment such as the ocean, rivers, lakes and marshes, and factory wastewater into the container 1. A water collecting pipe 5 is provided above the floating layer 2 in the container 1, and the treated water is collected by the water collecting pipe 5 and discharged from the drain pipe 6. In addition, a surplus sludge draining pipe 7 having a discharge valve 7a is provided at the bottom of the container 1, and a backwash nozzle 8 is provided in the middle layer of the container 1.

【0013】ここで、担持体2aは重量%で結晶性ポリ
プロピレン86%、非結晶性ポリプロピレン8%の合成
樹脂に発泡剤6%を加え、気泡の径が10μm〜10m
mとなるように独立発泡させ、その発泡体を破砕するこ
とにより得られた0.1mm〜300mmの径の多面体
の小片からなり、このような各種サイズの担持体2aを
多数浮遊させることにより浮遊層2をなしている。尚、
この担持体2aは異物を吸着する吸着材もなしている。
Here, the carrier 2a is made by adding 6% of a foaming agent to a synthetic resin of 86% of crystalline polypropylene and 8% of amorphous polypropylene by weight% so that the diameter of bubbles is 10 μm to 10 m.
It is composed of small pieces of polyhedron having a diameter of 0.1 mm to 300 mm obtained by independently foaming so as to have m and crushing the foam, and floating by suspending a large number of carriers 2a of various sizes. It is layer 2. still,
The carrier 2a also serves as an adsorbent that adsorbs foreign matter.

【0014】尚、本実施例では図示したように防臭とメ
タンガスなどの廃ガスの回収を考えて容器1を蓋付きと
し、その頂上部にガス回収管9を設けた。このガス回収
管9には水が溜まったUベントが設けられている。尚、
実際には容器1の上部を開口したままでも良い。
In this embodiment, as shown in the figure, the container 1 is provided with a lid in consideration of deodorization and recovery of waste gas such as methane gas, and a gas recovery pipe 9 is provided at the top thereof. The gas recovery pipe 9 is provided with a U vent in which water is collected. still,
In practice, the upper part of the container 1 may be left open.

【0015】容器1内の散水ノズル4の下部には余剰汚
泥及び微生物塊からなる嫌気造粒汚泥層10が形成さ
れ、散水ノズル4と浮遊層2との間には汚泥造粒帯11
が形成されるようになる。尚、符号19は担持体2aが
下部に流出することを防止するための吸着材または担持
体用分級板である。
An anaerobic granulation sludge layer 10 composed of excess sludge and microbial mass is formed below the water spray nozzle 4 in the container 1, and a sludge granulation zone 11 is formed between the water spray nozzle 4 and the floating layer 2.
Will be formed. Reference numeral 19 is an adsorbent or a carrier classifying plate for preventing the carrier 2a from flowing out to the lower part.

【0016】原水(異物含有液)を導入管3を介して散
水ノズル4より容器1内の下部から上に向けて流し込む
と、余剰汚泥及び微生物塊からなる嫌気造粒汚泥層1
0、汚泥造粒帯11を通過して、浮遊層2に至り、この
浮遊層2を通過して水面より集水管5にて集められて排
水管6から排出させる。ここで、汚泥造粒帯11水滞部
を通過する間にSS同士のぶつかり合いによる粗粒化が
促進され、また微生物により自己造粒されて嫌気造粒汚
泥層10が形成され、異物含有液は嫌気造粒汚泥層10
により濾過された後、汚泥造粒帯11を通過して浮遊層
2の各担持体(吸着材)2a及びその内部に担持された
微生物により二重に濾過され、その間に有機物の微生物
分解と硝化とが行われる。
When raw water (liquid containing foreign matter) is poured from the lower part of the container 1 upward through the sprinkling nozzle 4 through the introduction pipe 3, the anaerobic granulated sludge layer 1 composed of excess sludge and microbial aggregates.
0, passes through the sludge granulation zone 11 to reach the floating layer 2, passes through the floating layer 2, is collected by the water collecting pipe 5 from the water surface, and is discharged from the drainage pipe 6. Here, coarsening due to collision of SSs is promoted while passing through the sludge granulation zone 11 stagnant portion, and anaerobic granulation sludge layer 10 is formed by self-granulation by microorganisms, and foreign matter-containing liquid Is anaerobic granulation sludge layer 10
After being filtered by the above, it is double filtered by each carrier (adsorbent) 2a of the floating layer 2 passing through the sludge granulation zone 11 and the microorganisms loaded therein, and during that time, microbial decomposition and nitrification of organic substances And are done.

【0017】次に、上記担持体2aの製造手順について
説明する。図2は、この担持体2aの発泡体を成形する
ためのガス抜き開口部付押出し混練器81の断面図であ
る。このガス抜き開口部付押出し混練器81は、シリン
ダ82と、その内部に設けられたスクリュー83と、原
料を投入するためにシリンダ82の基端に設けられたホ
ッパ84とを有している。シリンダ82の中間部には開
閉可能な蓋85が取付けられたベント82aが設けられ
ている。また、シリンダ82外周の適所にはヒータ86
が設けられ、シリンダ82内で原料が発泡し得る所望の
温度にシリンダ82を加熱し得るようになっている。こ
こで、シリンダ82の先端側は単に開口しているのみで
あり、ダイスなどは設けられていない。従って、このガ
ス抜き開口部付押出し混練器81に原料を投入すると、
比較的低圧でシリンダ82の開口82bから製品が押出
されることとなる。尚、開口82bの下方には冷却水の
溜められたプール87が設けられ、開口82bから押出
された製品を冷却するようになっている。
Next, a procedure for manufacturing the carrier 2a will be described. FIG. 2 is a cross-sectional view of an extrusion kneader 81 with a gas vent opening for molding the foam of the carrier 2a. The extrusion kneader 81 with a gas vent opening has a cylinder 82, a screw 83 provided inside the cylinder 82, and a hopper 84 provided at the base end of the cylinder 82 for charging raw materials. A vent 82a, to which an openable / closable lid 85 is attached, is provided at an intermediate portion of the cylinder 82. Further, a heater 86 is provided at an appropriate position on the outer periphery of the cylinder 82
Is provided so that the cylinder 82 can be heated to a desired temperature at which the raw material can foam in the cylinder 82. Here, the tip end side of the cylinder 82 is simply opened, and no die or the like is provided. Therefore, when the raw material is put into the extrusion kneader 81 with the gas vent opening,
The product will be extruded from the opening 82b of the cylinder 82 at a relatively low pressure. A pool 87 in which cooling water is stored is provided below the opening 82b to cool the product extruded from the opening 82b.

【0018】上記したように重量%で結晶性ポリプロピ
レン86%、非結晶性ポリプロピレン8%の合成樹脂に
発泡剤6%を加えた原料を、ホッパ84からガス抜き開
口部付押出し混練器81に投入すると、低圧でシリンダ
82内をスクリュ83により混練されつつ流動する。こ
のとき、上記原料はヒータ86により加熱され、また圧
力を調整されて気泡の径が10μm〜10mmとなるよ
うに発泡する。この発泡は低圧で混練しつつ行われるこ
とから独立発泡となり、原料内の気泡が独立気泡とな
る。
As described above, a raw material obtained by adding 6% of a foaming agent to a synthetic resin of 86% crystalline polypropylene and 8% amorphous polypropylene by weight% is charged from the hopper 84 into the extrusion kneader 81 with a gas vent opening. Then, at low pressure, it flows in the cylinder 82 while being kneaded by the screw 83. At this time, the raw material is heated by the heater 86, and the pressure is adjusted to foam the bubbles to have a diameter of 10 μm to 10 mm. Since this foaming is performed while kneading at a low pressure, it becomes independent foaming, and the bubbles in the raw material become independent bubbles.

【0019】このように独立発泡した製品は開口82b
から押出され、プール87にて冷却される。そして、図
示されない公知のクラッシャにより破砕され、0.1m
m〜300mmの径の多面体の小片からなる吸着材が完
成する。これを適性菌の担持体とするには、適性菌の存
在する溶液に漬けるなどしてこの適性菌を担持させれば
良い。
In this way, the independently foamed product has an opening 82b.
And is cooled in the pool 87. Then, it is crushed by a well-known crusher (not shown), and 0.1m
An adsorbent consisting of small pieces of polyhedron with a diameter of m to 300 mm is completed. In order to use this as a carrier for suitable bacteria, the suitable bacteria may be supported by immersing it in a solution containing the suitable bacteria.

【0020】尚、本実施例では原料として結晶性ポリプ
ロピレン86%、非結晶性ポリプロピレン8%の合成樹
脂に発泡剤6%を加えたものを用いたが、樹脂としてポ
リエチレン及び非結晶性ポリエチレンなどを用いても良
く、また、除去を必要とする異物が存在する排水の内容
成分によって最も適した樹脂素材を使用し、発泡させて
発泡体として用いても良い。更に、所望の割合でこぎり
くず、わらくず、穀物のもみがら、木片、繊維小片及び
不織布小片などの天然多孔質材を混入しても良い。この
場合、或る程度の気泡の確保が可能であると共に廃物利
用によるコスト軽減が期待できる。また、本実施例では
ガス抜き開口部付押出し混練器内にて独立発泡させた
が、通常の容器内に原料を投入し、加熱しつつ混練して
も同様な発泡体が得られる。
In this embodiment, a synthetic resin of 86% crystalline polypropylene and 8% amorphous polypropylene to which 6% of a foaming agent is added is used as a raw material, but polyethylene and amorphous polyethylene are used as the resin. It may be used, or may be used as a foam by using a resin material most suitable for the content component of the waste water in which foreign substances that need to be removed are present and foaming. Further, natural porous materials such as sawdust, sawdust, grain chaff, wood chips, fiber pieces, and non-woven cloth pieces may be mixed in a desired ratio. In this case, it is possible to secure a certain amount of bubbles, and it can be expected to reduce the cost by using waste. Further, in the present embodiment, the independent foaming was performed in the extrusion kneader with the gas vent opening, but the same foam can be obtained by charging the raw materials into a normal container and kneading while heating.

【0021】図3は、本発明が適用された第2の実施例
を示す嫌気性菌による処理装置を模式的に示す図であ
る。本実施に於ける嫌気性菌による処理装置本体は第1
の実施例と同様であるが、その排水管6が後段の脱窒槽
21内の下側散水ノズル24に接続されている。また、
排水管6の中間部に注入管6aを接続し、排水管6内に
処理水に微生物の増殖栄養剤を注入するようになってい
る。脱窒槽21には、浮遊層2と同様に微生物(適性
菌)を担持する見かけ比重または真比重が除去を必要と
する母液比重以下の多数の担持体22aを浮遊させてな
る脱窒層22が設けられている。脱窒槽21の脱窒層2
2の上部には集水管25及び該集水管25に接続された
排水管26が設けられている。尚、脱窒槽21は、その
上端から窒素ガスを外部に排出するようになっている。
FIG. 3 is a diagram schematically showing a treatment apparatus using anaerobic bacteria showing a second embodiment to which the present invention is applied. The main body of the anaerobic bacterium treatment equipment in this implementation is the first
However, the drainage pipe 6 is connected to the lower water spray nozzle 24 in the denitrification tank 21 at the latter stage. Also,
An injection pipe 6a is connected to an intermediate portion of the drain pipe 6 so that a microbial growth nutrient is injected into the treated water in the drain pipe 6. Like the floating layer 2, the denitrification tank 21 has a denitrification layer 22 formed by suspending a large number of carriers 22a whose apparent specific gravity or true specific gravity supporting microorganisms (appropriate bacteria) is equal to or less than the mother liquor specific gravity which needs to be removed. It is provided. Denitrification layer 2 of denitrification tank 21
A water collecting pipe 25 and a drain pipe 26 connected to the water collecting pipe 25 are provided on the upper portion of the water collecting pipe 2. The denitrification tank 21 discharges nitrogen gas from the upper end thereof.

【0022】排水管26はその後段の好気槽31内の下
側散水ノズル34に接続されている。この好気槽31に
は、浮遊層2と同様に微生物(適性菌)を担持する見か
け比重または真比重が除去を必要とする異物が存在する
母液比重以下の多数の担持体32aを浮遊させてなる好
気層32が設けられている。好気槽31の好気層32の
上部には集水管35及び該集水管35に接続された排水
管36が設けられている。
The drain pipe 26 is connected to the lower water spray nozzle 34 in the aerobic tank 31 at the subsequent stage. In the aerobic tank 31, as in the floating layer 2, a large number of carriers 32a having an apparent specific gravity or a true specific gravity for supporting microorganisms (appropriate bacteria) and a foreign matter that needs to be removed and is equal to or lower than the mother liquor specific gravity are suspended. The aerobic layer 32 is provided. A water collecting pipe 35 and a drain pipe 36 connected to the water collecting pipe 35 are provided above the aerobic layer 32 of the aerobic tank 31.

【0023】本実施例によれば、容器1にて嫌気性菌に
より処理され、硝化された異物含有液中の窒素が脱窒、
脱燐処理されて外部に排出されるようになる。それ以外
の構成は第1の実施例と同様である。
According to this embodiment, the nitrogen in the liquid containing nitrified foreign matter which has been treated with anaerobic bacteria in the container 1 is denitrified,
It is dephosphorized and discharged to the outside. The other configuration is the same as that of the first embodiment.

【0024】図4は、本発明が適用された第3の実施例
を示す嫌気性菌による処理装置を模式的に示す図であ
る。本実施の構成は概ね第2の実施例と同様であるが、
好気槽31からの排水管36に戻し管40が接続され、
処理水の一部を導入管3に循環させるようになってい
る。これにより原水のBOD(指標要因物質)を活用し
て微生物を増殖させ、脱窒を促進するようになってい
る。それ以外の構成は第2の実施例と同様である。
FIG. 4 is a diagram schematically showing a treatment apparatus using anaerobic bacteria showing a third embodiment to which the present invention is applied. The configuration of this embodiment is almost the same as that of the second embodiment,
The return pipe 40 is connected to the drain pipe 36 from the aerobic tank 31,
A part of the treated water is circulated through the introduction pipe 3. As a result, the BOD (index factor substance) of raw water is utilized to grow microorganisms and accelerate denitrification. The other structure is similar to that of the second embodiment.

【0025】尚、上記各実施例では本発明吸着材及び担
持体を容器内に充填したが、母液に単に浮遊させても良
い。この場合、吸着材の気泡内に、表面張力及び毛細管
現象により異物が充分に吸着される所定時間経過後に吸
着済みの吸着材を回収すれば良い。
Although the adsorbent of the present invention and the carrier are filled in the container in each of the above-mentioned embodiments, they may be simply suspended in the mother liquor. In this case, the adsorbent that has been adsorbed may be collected after a lapse of a predetermined time in which the foreign matter is sufficiently adsorbed in the bubbles of the adsorbent due to the surface tension and the capillary phenomenon.

【0026】図5は、本発明が適用された第4の実施例
を示す廃液処理装置を模式的に示す図である。本実施例
は海洋、河川、湖沼、工場排水初期受槽底(沈澱槽)等
に含まれる浮遊沈澱物と、液状物質とを分取する廃液処
理装置に本発明吸着材及び担持体を用いたものである。
図に於て容器51は、上部が大径であり、かつ下部が小
径の概ね逆円錐形をなす下部体51aと、下部体51a
の底部とやや離間して対向する開口を有する有底筒状の
上部体51bとから構成されている。下部体の縮径する
底部にはドレンバルブ51cが設けられている。上部体
51b内には抑止板53が設けられ、その下部に見かけ
比重または真比重が回収または除去を必要とする異物が
存在する母液の比重以下の浮遊充填材としての吸着濾過
分離材52aを充填し、浮遊層52を形成している。上
部体51bの中間部には容器51内に廃液を流し込むべ
く、水量調整槽55に接続されると共に中間部にUベン
ト56及び逆流防止電磁弁57が設けられた導入管54
が開口している。また、浮遊層52にて造粒される多量
のスラッジを支障なく排出するべく上部体51bの下端
開口は全開され、下部体51aの縮径する底部に集めら
れ、ドレンバルブ51cを開放することにより外部に排
出されるようになっている。加えて、上部体51bの上
端には処理水を排水するための排水管58が開口してい
る。ここで、排水管56には図示されないポンプが接続
され、水面が下部体51aからあふれないように、上部
体51bの頂部から排水管58まで常に水が充満するよ
うに調整されている。
FIG. 5 is a diagram schematically showing a waste liquid treatment apparatus showing a fourth embodiment to which the present invention is applied. In this embodiment, the adsorbent and the carrier of the present invention are used in a waste liquid treatment device for separating a floating substance and a liquid substance contained in the bottom (precipitation tank) of the initial receiving tank (precipitation tank) of the ocean, rivers, lakes and marshes. Is.
In the figure, a container 51 has a lower body 51a and a lower body 51a, each of which has a large diameter at the upper portion and a small diameter at the lower portion and has a substantially inverted conical shape.
And a bottomed tubular upper body 51b having an opening that faces the bottom of the above with a slight distance therebetween. A drain valve 51c is provided on the bottom of the lower body where the diameter is reduced. A suppression plate 53 is provided in the upper body 51b, and an adsorption filtration separation material 52a as a floating packing material whose apparent specific gravity or true specific gravity is below the specific gravity of the mother liquor in which foreign substances need to be collected or removed is filled under the suppression plate 53. Then, the floating layer 52 is formed. Introducing pipe 54, which is connected to a water amount adjusting tank 55 and has a U vent 56 and a backflow prevention solenoid valve 57 in the intermediate portion, in order to flow the waste liquid into container 51, in the middle portion of upper body 51b.
Is open. In addition, the lower end opening of the upper body 51b is fully opened to collect a large amount of sludge that is granulated in the floating layer 52 without any hindrance, and the lower body 51a is collected at the reduced bottom of the lower body 51a, and the drain valve 51c is opened. It is designed to be discharged to the outside. In addition, a drain pipe 58 for draining the treated water is opened at the upper end of the upper body 51b. Here, a pump (not shown) is connected to the drain pipe 56 and is adjusted so that the water surface does not overflow from the lower body 51a and the water is constantly filled from the top of the upper body 51b to the drain pipe 58.

【0027】実際に廃液を処理するには、導入管54か
ら廃液を容器51内に流し込む。すると、浮遊層52に
て浮遊沈澱物(異物)と液体とが分離され、液体は清澄
水として排水管58から排出され、浮遊沈澱物は粗粒化
されて、更に増大して下部体51aの縮径する底部に集
められる。そして、ドレンバルブ51cを開放すること
によりこれが外部に排出される。ここで、吸着濾過分離
材52aは第1〜第3の実施例と同様に重量%で結晶性
ポリプロピレン86%、非結晶性ポリプロピレン8%の
合成樹脂に発泡剤6%を加え、気泡の径が10μm〜1
0mmとなるように独立発泡させ、その発泡体を破砕す
ることにより得られた0.1mm〜300mmの径の多
面体の小片からなり、このような各種サイズの吸着濾過
分離材52aを多数浮遊させることにより浮遊層52を
なしている。本発明吸着材はこのような利用法もある。
To actually treat the waste liquid, the waste liquid is poured into the container 51 through the introduction pipe 54. Then, the floating sediment (foreign matter) and the liquid are separated in the floating layer 52, and the liquid is discharged as clear water from the drain pipe 58, and the floating sediment is coarse-grained and further increased to increase in the lower body 51a. Collected at the shrinking bottom. Then, by opening the drain valve 51c, this is discharged to the outside. Here, as in the case of the first to third embodiments, the adsorptive filtration separation material 52a has a foaming agent of 6% added to a synthetic resin of 86% of crystalline polypropylene and 8% of amorphous polypropylene by weight% so that the diameter of bubbles is 10 μm to 1
It is composed of small pieces of polyhedron having a diameter of 0.1 mm to 300 mm obtained by crushing the foam independently foamed to 0 mm, and floating a large number of adsorption filtration separation materials 52a of various sizes. Thus forming the floating layer 52. The adsorbent of the present invention can also be used in this way.

【0028】図6は、本発明が適用された第5の実施例
を示す気液接触を行い得る無菌による濾過、または適性
菌との接触による上向流型の廃液処理装置を模式的に示
す図である。図に於て容器61内には抑止板63が設け
られ、その下部に微生物(適性菌)を担持する見かけ比
重または真比重が回収または除去を必要とする異物の存
在する母液比重以下の担持体62a(浮遊充填材)を充
填し、浮遊層62を形成している。容器61の下部には
空気を容器61内に流し込む(曝気する)べく導入管6
4が開口すると共に容器61内に廃液を流し込むための
導入管65が設けられている。また、容器1の上部に
は、処理水を排水するための排水管66が開口してい
る。尚、符号69は担持体62aが下部に流出すること
を防止するための吸着材または担持体用分級板である。
FIG. 6 schematically shows a fifth embodiment to which the present invention is applied, which is an upflow-type waste liquid treatment apparatus by aseptic filtration capable of performing gas-liquid contact or contact with a suitable bacterium. It is a figure. In the figure, a container 61 is provided with a deterrent plate 63, and a carrier having an apparent specific gravity or a true specific gravity for supporting microbes (appropriate bacteria) below the mother liquor specific gravity in which foreign substances that need to be collected or removed exist. 62a (floating filler) is filled to form the floating layer 62. In the lower part of the container 61, an introduction pipe 6 is provided to inject (aerate) air into the container 61.
4 is opened and an introduction pipe 65 for pouring the waste liquid into the container 61 is provided. Further, a drain pipe 66 for draining the treated water is opened at the upper part of the container 1. In addition, reference numeral 69 is an adsorbent or a classifying plate for a carrier for preventing the carrier 62a from flowing out to the lower part.

【0029】実際に廃液を処理するには、導入管64か
ら空気を容器61内に流し込みつつ導入管65から廃液
を容器61内に流し込む。すると、浮遊層62にて廃液
と空気とが好適に接触し、廃液が浄化される。ここで、
担持体62aは第1〜第4の実施例と同様に重量%で結
晶性ポリプロピレン86%、非結晶性ポリプロピレン8
%の合成樹脂に発泡剤6%を加え、気泡の径が10μm
〜10mmとなるように独立発泡させ、その発泡体を破
砕することにより得られた0.1mm〜300mmの径
の多面体の小片からなり、このような各種サイズの担持
体62aを多数浮遊させることにより浮遊層62をなし
ている。
To actually treat the waste liquid, the waste liquid is allowed to flow into the container 61 from the introduction pipe 65 while the air is allowed to flow from the introduction pipe 64 into the container 61. Then, the waste liquid and the air are appropriately brought into contact with each other in the floating layer 62, and the waste liquid is purified. here,
As in the first to fourth embodiments, the carrier 62a is 86% by weight of crystalline polypropylene and 8% by weight of amorphous polypropylene.
% Synthetic resin with 6% foaming agent to give a bubble diameter of 10 μm
It is composed of small pieces of polyhedron having a diameter of 0.1 mm to 300 mm obtained by crushing the foam independently by independently foaming so as to have a size of -10 mm. It forms the floating layer 62.

【0030】図7は、本発明が適用された第6の実施例
を示す気液接触を行い得る母液比重以下の異物を有する
母液の下降流型の廃液処理装置を模式的に示す図であ
る。図に於て容器71内には抑止板73が設けられ、そ
の下部に微生物(適性菌)を担持する見かけ比重または
真比重が回収または除去を必要とする異物の存在する母
液比重以下の担持体72a(浮遊充填材)を充填し、浮
遊層72を形成している。容器71の下部には空気を容
器71内に流し込む(曝気する)べく導入管74が開口
すると共に処理水を排水するための排水管75が開口し
ている。また、容器71の上端には該容器71内に廃液
を流し込むための導入管76及び分離した異物を外部に
排出するための排出管77が設けられ、浮遊層72の上
部には水の層Wを介して多数の孔が設けられた廃液分散
板78が設けられている。尚、符号79は担持体72a
が下部に流出することを防止するための吸着材または担
持体用分級板であり、符号Oは分離した異物の層であ
る。
FIG. 7 is a diagram schematically showing a sixth embodiment of the present invention, in which a mother liquor downward flow type waste liquid treatment apparatus having foreign matter having a specific gravity of the mother liquor or less capable of performing gas-liquid contact is used. . In the figure, a container 71 is provided with a restraining plate 73, and a carrier having an apparent specific gravity or true specific gravity for supporting microorganisms (appropriate bacteria) below the mother liquor in which foreign substances that need to be collected or removed exist. 72a (floating filler) is filled to form the floating layer 72. In the lower part of the container 71, an introduction pipe 74 is opened to let air flow into the container 71 (aeration), and a drain pipe 75 for discharging treated water is opened. Further, an inlet pipe 76 for pouring the waste liquid into the container 71 and a discharge pipe 77 for discharging the separated foreign matter to the outside are provided at the upper end of the container 71, and a water layer W is provided above the floating layer 72. A waste liquid dispersion plate 78 having a large number of holes is provided. Incidentally, reference numeral 79 is a carrier 72a.
Is a classifying plate for an adsorbent or a carrier for preventing the particles from flowing out to the lower part, and a symbol O is a layer of separated foreign matter.

【0031】実際に廃液を処理するには、導入管74か
ら空気を容器71内に流し込みつつ導入管76から廃液
を容器71内に流し込む。すると、浮遊層72にて廃液
と空気とが好適に接触し、廃液が浄化される。ここで、
担持体72aは第1〜第5の実施例と同様に重量%で結
晶性ポリプロピレン86%、非結晶性ポリプロピレン8
%の合成樹脂に発泡剤6%を加え、気泡の径が10μm
〜10mmとなるように独立発泡させ、その発泡体を破
砕することにより得られた0.1mm〜300mmの径
の多面体の小片からなり、このような各種サイズの担持
体72aを多数浮遊させることにより浮遊層72をなし
ている。更に図7の下降流と図6の上向流とを併用する
ことにより、母液比重の小さい汚染物質と母液より比重
の大きい汚染物質とを分取することかできる。
To actually treat the waste liquid, the waste liquid is poured into the container 71 through the introduction pipe 76 while the air is introduced through the introduction pipe 74 into the container 71. Then, the waste liquid and the air are appropriately brought into contact with each other in the floating layer 72, and the waste liquid is purified. here,
The carrier 72a is 86% by weight of crystalline polypropylene and 8% by weight of amorphous polypropylene as in the first to fifth embodiments.
% Synthetic resin with 6% foaming agent to give a bubble diameter of 10 μm
It is composed of small pieces of polyhedron having a diameter of 0.1 mm to 300 mm obtained by crushing the foam independently foamed to 10 mm, and by suspending a large number of carriers 72a of various sizes. It forms the floating layer 72. Further, by using the downward flow of FIG. 7 and the upward flow of FIG. 6 together, it is possible to separate the pollutant having a smaller specific gravity of the mother liquor and the pollutant having a larger specific gravity than the mother liquor.

【0032】ここで、上記した下降流型の廃液処理装置
を利用してナフサ、灯油または各種溶剤を異物を移行さ
せるための抽出剤とし、回収または除去が必要な異物を
含む母液を注入し、異物の下方流出を防止するために本
発明吸着材を設置すれば、目的とする異物を選択的に回
収または除去することができる。例えば回収し難い放射
性物質及び金属イオン交換後の固体の非鉄金属液等を分
取し、これが再びイオン化することを防止するのに適し
ている。
Here, naphtha, kerosene or various solvents are used as an extractant for transferring foreign substances by using the above-mentioned downflow type waste liquid treatment device, and mother liquor containing foreign substances which need to be recovered or removed is injected. If the adsorbent of the present invention is installed in order to prevent downward flow of foreign matter, the desired foreign matter can be selectively collected or removed. For example, it is suitable for collecting radioactive substances that are difficult to recover and solid non-ferrous metal liquids after metal ion exchange and the like and preventing them from being ionized again.

【0033】[0033]

【発明の効果】以上の説明により明らかなように本発明
によれば、独立発泡による独立気泡を有する見かけ比重
または真比重が母液の比重以下の発泡体からなる吸着材
または適性菌の担持体を母液に接触させるのみで、海
洋、河川、湖沼、工場排水等、処理を必要とする例えば
BOD、COD、SS等の異物を含むあらゆる異物含有
液(母液)を効率的かつ効果的に浄化可能であり、滞留
時間の短縮化が可能となる。また、吸着材及び担持体が
浮遊することから、例えばこの吸着材及び担持体を用い
た場合、装置を横方向のみでなく上下方向に延ばすこと
ができることから設置面積を低減することができ、装置
の小型化を計ることができる。また、この吸着材または
適性菌の担持体が、上記発泡体を破砕することにより得
られる形成された大きさ及び形状の不揃いな多数の小片
からなることにより、母液との接触効率が向上する。更
に、この吸着材または適性菌の担持体に天然多孔質材を
混入した場合、或る程度の気泡の確保が可能であると共
に廃物利用によるコスト軽減が期待できる。
As is apparent from the above description, according to the present invention, an adsorbent or a carrier of a suitable bacterium, which is a foam having an apparent specific gravity or a true specific gravity of the closed liquor by the independent foaming, is equal to or less than the specific gravity of the mother liquor. It is possible to efficiently and effectively purify all foreign matter-containing liquids (mother liquor) containing foreign substances such as BOD, COD, SS, etc. that require treatment, such as the ocean, rivers, lakes and marshes, factory wastewater, etc., simply by contacting them with mother liquor. Therefore, the residence time can be shortened. Further, since the adsorbent and the carrier float, for example, when the adsorbent and the carrier are used, the device can be extended not only in the horizontal direction but also in the vertical direction, so that the installation area can be reduced and the device can be reduced. Can be miniaturized. Further, since the adsorbent or the carrier of the suitable bacteria is composed of a large number of small pieces having irregular sizes and shapes formed by crushing the foam, the contact efficiency with the mother liquor is improved. Furthermore, when a natural porous material is mixed in the adsorbent or a support for suitable bacteria, it is possible to secure a certain amount of bubbles and reduce the cost by using waste.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明が適用された第1の実施例を示す嫌気性
菌による処理装置のダイヤグラム図である。
FIG. 1 is a diagrammatic view of a treatment apparatus using anaerobic bacteria showing a first embodiment to which the present invention is applied.

【図2】本発明に基づく独立気泡を有する発泡体からな
る吸着材または適性菌の担持体の製造手順を示すガス抜
き開口部付押出し混練器の断面図である。
FIG. 2 is a cross-sectional view of an extrusion kneader with a gas vent opening showing a procedure for manufacturing an adsorbent or a support for suitable bacteria, which is made of a foam having closed cells according to the present invention.

【図3】本発明が適用された第2の実施例を示す図1と
同様な嫌気性菌による処理装置のダイヤグラム図であ
る。
FIG. 3 is a diagrammatic view of a treatment apparatus using anaerobic bacteria similar to FIG. 1, showing a second embodiment to which the present invention is applied.

【図4】本発明が適用された第3の実施例を示す図1及
び図3と同様な嫌気性菌による処理装置のダイヤグラム
図である。
FIG. 4 is a diagrammatic view of a treatment apparatus using anaerobic bacteria similar to FIGS. 1 and 3, showing a third embodiment to which the present invention is applied.

【図5】本発明が適用された第4の実施例を示す上向流
高比重大容量スラッジ除去装置のダイヤグラム図であ
る。
FIG. 5 is a diagrammatic view of an upflow high specific capacity sludge removing device showing a fourth embodiment to which the present invention is applied.

【図6】本発明が適用された第5の実施例を示す母液比
重以上の異物を主として有する母液の無菌による濾過ま
たは適性菌との接触による上向流処理装置のダイヤグラ
ム図である。
FIG. 6 is a diagrammatic view of an upflow treatment apparatus according to a fifth embodiment of the present invention, in which a mother liquor mainly containing foreign matter having a specific gravity of the mother liquor or more is aseptically filtered or contacted with a suitable bacterium.

【図7】本発明が適用された第6の実施例を示す母液比
重以下の異物を有する母液の下降流処理装置のダイヤグ
ラム図である。
FIG. 7 is a diagrammatic view of a downward flow treatment device for mother liquor having foreign matter having a specific gravity of mother liquor or less, showing a sixth embodiment to which the present invention is applied.

【符号の説明】[Explanation of symbols]

1 容器 2 浮遊層 2a 担持体 3 導入管 4 散水ノズル 5 集水管 6 排水管 7 余剰汚泥抜き管 7a 排出弁 8 ノズル 9 ガス回収管 10 嫌気造粒汚泥層 11 汚泥造粒帯 13 抑止板 19 吸着材または担持体用分級板 21 脱窒槽 22 脱窒層 22a 担持体 24 散水ノズル 25 集水管 26 排水管 31 好気槽 32a 担持体 32 好気層 34 散水ノズル 35 集水管 36 排水管 40 戻し管 51 容器 51a 下部体 51b 上部体 51c ドレンバルブ 52 浮遊層 52a 吸着濾過分離材 53 抑止板 54 導入管 55 水量調整槽 56 Uベント 57 逆流防止電磁弁 58 排水管 61 容器 62 浮遊層 62a 担持体 63 抑止板 64 導入管 65 導入管 66 排水管 69 吸着材または担持体用分級板 71 容器 72 浮遊層 72a 担持体 73 抑止板 74 導入管 75 排水管 76 導入管 77 排出管(回収管) 78 廃液分散板 79 吸着材または担持体用分級板 W 水の層 O 異物の層 81 ガス抜き開口部付押出し混練器 82 シリンダ 82a ベント 82b 開口 83 スクリュー 84 ホッパ 85 蓋 86 ヒータ 87 プール 1 Container 2 Floating Layer 2a Carrier 3 Introducing Pipe 4 Sprinkling Nozzle 5 Water Collection Pipe 6 Drainage Pipe 7 Excess Sludge Drain Pipe 7a Discharge Valve 8 Nozzle 9 Gas Recovery Pipe 10 Anaerobic Granulation Sludge Layer 11 Sludge Granulation Zone 13 Suppression Plate 19 Adsorption Classification plate for material or carrier 21 Denitrification tank 22 Denitrification layer 22a Carrier 24 Water sprinkling nozzle 25 Water collecting pipe 26 Drain pipe 31 Aerobic tank 32a Carrier 32 Aerobic layer 34 Water sprinkling nozzle 35 Water collecting pipe 36 Drain pipe 40 Return pipe 51 Container 51a Lower body 51b Upper body 51c Drain valve 52 Floating layer 52a Adsorption filtration separation material 53 Suppression plate 54 Introducing pipe 55 Water amount adjusting tank 56 U vent 57 Backflow prevention solenoid valve 58 Drain pipe 61 Container 62 Floating layer 62a Carrier 63 Suppression plate 64 introduction pipe 65 introduction pipe 66 drainage pipe 69 adsorbent or carrier classifying plate 71 container 72 floating layer 72a Holding body 73 Suppression plate 74 Inlet pipe 75 Drain pipe 76 Inlet pipe 77 Discharge pipe (recovery pipe) 78 Waste liquid dispersion plate 79 Adsorbent or carrier classifying plate W Water layer O Foreign material layer 81 Extrusion kneading with degassing opening Container 82 Cylinder 82a Vent 82b Opening 83 Screw 84 Hopper 85 Lid 86 Heater 87 Pool

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 回収または除去を必要とする異物が存在
する母液に接触させることにより前記母液に含まれる異
物を吸着する異物吸着材であって、 独立発泡による独立気泡を有する見かけ比重または真比
重が前記母液の比重以下の発泡体からなることを特徴と
する異物吸着材。
1. A foreign matter adsorbent that adsorbs foreign matter contained in the mother liquor by bringing it into contact with a mother liquor containing foreign matter that needs to be recovered or removed, and has an apparent specific gravity or true specific gravity having independent bubbles due to independent foaming. Is a foam having a specific gravity of the mother liquor or less.
【請求項2】 回収または除去を必要とする異物が存在
する母液に含まれる異物を分解するための適性菌を担持
させるための担持体であって、 独立発泡による独立気泡を有する見かけ比重または真比
重が前記母液の比重以下の発泡体からなることを特徴と
する適性菌の担持体。
2. A carrier for supporting a suitable bacterium for decomposing foreign matter contained in a mother liquor in which a foreign matter requiring recovery or removal exists, the apparent specific gravity or true particle having closed cells by independent foaming. A carrier for a suitable bacterium, comprising a foam having a specific gravity not higher than that of the mother liquor.
【請求項3】 前記発泡体を破砕することにより形成さ
れた大きさ及び形状の不揃いな多数の小片からなること
を特徴とする請求項1に記載の異物吸着材。
3. The foreign matter adsorbing material according to claim 1, wherein the foreign matter adsorbing material is composed of a large number of small pieces having irregular sizes and shapes formed by crushing the foam.
【請求項4】 前記発泡体を破砕することにより形成さ
れた大きさ及び形状の不揃いな多数の小片からなること
を特徴とする請求項2に記載の適性菌の担持体。
4. The carrier of a suitable bacterium according to claim 2, comprising a large number of small pieces having irregular sizes and shapes formed by crushing the foam.
【請求項5】 前記発泡体が、天然多孔質材の混ざった
樹脂発泡体からなることを特徴とする請求項1に記載の
異物吸着材。
5. The foreign matter adsorbing material according to claim 1, wherein the foam comprises a resin foam mixed with a natural porous material.
【請求項6】 前記天然多孔質材がのこぎりくず、わら
くず、穀物のもみがら、木片、繊維小片及び不織布小片
のうちいずれか1つ若しくは2つ以上からなり、 前記発泡体が、前記天然多孔質材に発泡剤を混入した樹
脂材を発泡させてなることを特徴とする請求項5に記載
の異物吸着材。
6. The natural porous material comprises one or more of sawdust, sawdust, grain chaff, wood chips, fiber pieces and non-woven cloth pieces, and the foam is the natural porous material. The foreign matter adsorbing material according to claim 5, which is formed by foaming a resin material in which a foaming agent is mixed with a quality material.
【請求項7】 前記発泡体が、天然多孔質材の混ざった
樹脂発泡体からなることを特徴とする請求項2に記載の
担持体。
7. The carrier according to claim 2, wherein the foam comprises a resin foam mixed with a natural porous material.
【請求項8】 前記天然多孔質材がのこぎりくず、わら
くず、穀物のもみがら、木片、繊維小片及び不織布小片
のうちいずれか1つ若しくは2つ以上からなり、 前記発泡体が、前記天然多孔質材に発泡剤を混入した樹
脂材を発泡させてなることを特徴とする請求項7に記載
の担持体。
8. The natural porous material comprises any one or more of sawdust, sawdust, grain chaff, wood pieces, fiber pieces and non-woven piece pieces, and the foam is the natural porous material. The carrier according to claim 7, which is formed by foaming a resin material in which a foaming agent is mixed with a quality material.
【請求項9】 回収または除去を必要とする異物が存在
する母液に接触させることにより前記母液に含まれる異
物を吸着する異物吸着材の製造方法であって、 原料の樹脂材を混練しつつ独立発泡させ、内部に独立気
泡を形成する過程を有することを特徴とする異物吸着材
の製造方法。
9. A method for producing a foreign matter adsorbent for adsorbing a foreign matter contained in the mother liquor by contacting the mother liquor containing the foreign matter requiring recovery or removal, the method being independent while kneading a raw material resin material. A method for producing a foreign matter adsorbent, comprising the step of foaming and forming closed cells inside.
【請求項10】 回収または除去を必要とする異物が存
在する母液に含まれる異物を分解するための適性菌を担
持させるための担持体の製造方法であって、 原料の樹脂材を混練しつつ独立発泡させ、内部に独立気
泡を形成する過程を有することを特徴とする適性菌の担
持体の製造方法。
10. A method for producing a carrier for supporting a suitable bacterium for decomposing foreign matter contained in a mother liquor containing foreign matter requiring recovery or removal, which comprises kneading a resin material as a raw material. A method for producing a carrier for a suitable bacterium, which comprises a step of forming independent bubbles and forming closed cells inside.
JP5218113A 1993-08-10 1993-08-10 Method for producing foreign matter adsorbent and carrier of suitable bacteria Expired - Lifetime JP2726376B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5218113A JP2726376B2 (en) 1993-08-10 1993-08-10 Method for producing foreign matter adsorbent and carrier of suitable bacteria

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5218113A JP2726376B2 (en) 1993-08-10 1993-08-10 Method for producing foreign matter adsorbent and carrier of suitable bacteria

Publications (2)

Publication Number Publication Date
JPH0751690A true JPH0751690A (en) 1995-02-28
JP2726376B2 JP2726376B2 (en) 1998-03-11

Family

ID=16714837

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2726376B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010184177A (en) * 2009-02-10 2010-08-26 Yanmar Co Ltd Biofilter apparatus and land cultivation system
CN106049384A (en) * 2016-05-25 2016-10-26 安徽普氏生态环境工程有限公司 Centralized processing system for suspended matters in water body

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014200756A (en) * 2013-04-08 2014-10-27 三和化工株式会社 Filter medium and method of producing the same

Citations (7)

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Publication number Priority date Publication date Assignee Title
JPS5290159A (en) * 1976-01-22 1977-07-28 Matsushita Electric Works Ltd Waste water purifing device
JPS5524955A (en) * 1978-08-11 1980-02-22 Babcock Hitachi Kk Blast furnace slag treatment equipment
JPS5565198U (en) * 1978-10-28 1980-05-06
JPS63182130A (en) * 1987-01-23 1988-07-27 Japan Styrene Paper Co Ltd Manufacture of platelike foam of polyolefin resin
JPH02126905A (en) * 1988-11-04 1990-05-15 Nanyou Kyokai Method and apparatus for removing suspended solid with foamed plastic granule
JPH02273595A (en) * 1989-04-14 1990-11-08 Mitsui Petrochem Ind Ltd Immobilizing material for bacterial cell
JPH05117501A (en) * 1991-10-25 1993-05-14 Kanegafuchi Chem Ind Co Ltd Polyethylene terephthalate-based resin composition and production of foam using the same

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5290159A (en) * 1976-01-22 1977-07-28 Matsushita Electric Works Ltd Waste water purifing device
JPS5524955A (en) * 1978-08-11 1980-02-22 Babcock Hitachi Kk Blast furnace slag treatment equipment
JPS5565198U (en) * 1978-10-28 1980-05-06
JPS63182130A (en) * 1987-01-23 1988-07-27 Japan Styrene Paper Co Ltd Manufacture of platelike foam of polyolefin resin
JPH02126905A (en) * 1988-11-04 1990-05-15 Nanyou Kyokai Method and apparatus for removing suspended solid with foamed plastic granule
JPH02273595A (en) * 1989-04-14 1990-11-08 Mitsui Petrochem Ind Ltd Immobilizing material for bacterial cell
JPH05117501A (en) * 1991-10-25 1993-05-14 Kanegafuchi Chem Ind Co Ltd Polyethylene terephthalate-based resin composition and production of foam using the same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010184177A (en) * 2009-02-10 2010-08-26 Yanmar Co Ltd Biofilter apparatus and land cultivation system
CN106049384A (en) * 2016-05-25 2016-10-26 安徽普氏生态环境工程有限公司 Centralized processing system for suspended matters in water body

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